Gavage In Corn Oil Research Articles

Toxicity studies of 1,3-dichlorobenzene in Sprague-Dawley rats.

Male and female Sprague-Dawley rats received 1,3-dichlorobenzene daily by corn oil gavage for 10 or 90 consecutive days. The 10-day study doses were 0, 37, 147, 368 and 735 mg/kg; the 90-day study doses were 0, 9, 37, 147 and 588 mg/kg. In the 10-day study, there was a significant depression of body weight in both sexes at 735 mg/kg. Liver weights were significantly increased in both sexes at 368 and 735 mg/kg. Serum cholesterol levels were significantly elevated in both sexes at 368 and 735 mg/kg. Histopathological evaluation revealed centrolobular hepatocellular degeneration at 368 mg/kg in males and 735 mg/kg in females. In the 90-day study, body weights were significantly depressed in both sexes at 588 mg/kg. Normalization of food and water consumption by final body weight indicated that at 588 mg/kg both sexes had increased food and water consumption relative to controls. Absolute and relative liver weights were significantly increased in both sexes at 147 and 588 mg/kg. Relative kidney weights were significantly higher in both sexes at 588 mg/kg and in males at 147 mg/kg. Serum cholesterol and calcium levels were significantly elevated over controls in females at 37, 147, and 588 mg/kg, and in males at all dose levels. Histopathological evaluation at 147 and/or 588 mg/kg demonstrated liver and thyroid lesions in both sexes, and pituitary and kidney lesions in males. A NOAEL was not firmly established.

Comparison of the toxicity of cinnamaldehyde when administered by microencapsulation in feed or by corn oil gavage

The toxicity of cinnamaldehyde (CNMA) was compared after administration by gavage and in dosed feed. Rats and mice of both sexes received CNMA by daily corn oil gavage (for 2 wk), or in microencapsulated form in feed (2 wk for rats, 3 wk for mice). Feed formulations contained 0–10% CNMA microcapsules, equivalent to approximate daily doses of 0–3000 mg CNMA/kg body weight for rats and 0–10,000 mg CNMA/kg body weight for mice. Concentrations were chosen to deliver CNMA doses approximately equal to doses in the gavage study. Gavage doses of 2620 mg/kg/day and above in mice and 940 mg/kg/day and above in rats produced nearly 100% mortality; there were no deaths in animals receiving microencapsulated CNMA. Rats and mice receiving CNMA in feed showed a dose-related decrease in body weight gain, which was accompanied in rats by hypoplastic changes in reproductive organs and accessory sex glands. CNMA administration by either route caused hyperplasia of the forestomach mucosa. These results demonstrate that microencapsulation in feed can present a useful alternative to gavage dosing for repeated-dose or prolonged-exposure studies, in that (1) the toxic effects of CNMA were similar after gavage dosing and after administration in microencapsulated form in feed, (2) ingestion of chemical in the feed more closely approximates human exposures, and (3) microencapsulation allows the delivery of higher net doses of chemical, while avoiding the acutely toxic effects of a bolus dose.

Investigations of the genotoxicity and cell proliferative activity of dichlorvos in mouse forestomach

This study investigated the possible mechanism by which dichlorvos may have caused forestomach tumours in mice in a chronic corn oil gavage cancer bioassay [NTP (1989) Toxicology and carcinogenesis studies of dichlorvos in F344/N rats and B6C3F1 mice (gavage studies). National Toxicology Program Technical Report 342, NIH Publ. No 89-2598]. For this purpose, a method has been developed to assess the genetoxicity of irritant substances on mouse forestomach epithelium. Groups of five B6C3F1 mice were given a single oral dose of dichlorbos, the genotoxic forestomach carcinogen 1-methyl-3-nitro-1-nitrosoguanidine (MNNG) or the irritant, non-genotoxic forestomach carcinogen butylated hydroxyanisole (BHA). After periods of 2–48 h, three parameters were assessed: unscheduled DNA synthesis (UDS) by autoradiography of tissue sections, replicative DNA synthesis (RDS) also by autoradiography of incorporated [ 3H]thymidine, and histopathological changes, including hyperplasia. MNNG induced UDS but not RDS or hyperplasia in forestomach eptthelium consistent with its genotoxic mode of action. BHA and dichlorvos did not induce UDS, consistent with absence of genotoxic activity in the forestomach after in vivo exposure. In contrast, BHA and dichlorvos induced RDS and subsequent hyperplasia, which is likely to result from irritant damage. These data suggest that the chronic effects of dichlorvos on mouse forestomach epithelium in the oral gavage bioassay were mediated via enforced cell proliferation, rather than a genotoxic mechanism.

Route of Administration Determines Whether Chloroform Enhances or Inhibits Cell Proliferation in the Liver of B6C3F1 Mice

Route of Administration Determines Whether Chloroform Enhances or Inhibits Cell Proliferation in the Liver of B6C3F1 Mice. Pereira, M. A. (1994). Fundam. Appl. Toxicol. 23, 8792.Chloroform administered by garage has been shown to induce liver cancer in B6C3F1 mice; however, when administered in the drinking water, chloroform inhibited liver cancer in mice. The effect of chloroform administered by these two routes upon cell proliferation in mouse liver was determined. Female B6C3F1 mice were divided into five treatment groups: (1) chloroform (263 mg/kg body wt) by gavage in corn oil, (2) 1800 ppm chloroform in drinking water, (3) 1800 ppm chloroform in drinking water plus 10 ml/kg body wt corn oil by gavage, (4) 10 ml/kg body wt corn oil by gavage, and (5) untreated controls. Five days prior to termination, the mice were implanted subcutaneously with a 7-day osmotic minipump containing 30 mg/ml bromodeoxyuridine. Mice were terminated after 5, 12, 33, and 159 days of exposure. Chloroform administered by gavage in corn oil increased cell proliferation at all terminations, while, when administered in drinking water, cell proliferation was inhibited on Days 5 and 12. At 33 and 159 days, chloroform administered in the drinking water did not affect cell proliferation, even though the dose received by the animals was comparable to that given in corn oil by gavage. Therefore, cell proliferation was enhanced only by chloroform administered in corn oil by gavage, which corresponds to the hepatocarcinogenicity of chloroform administered by this route.

Induced Cytotoxicity and Cell Proliferation in the Hepatocarcinogenicity of Chloroform in Female B6C3F1 Mice: Comparison of Administration by Gavage in Corn Oil vs ad Libitum in Drinking Water

Induced Cytotoxicity and Cell Proliferation in the Hepatocarcinogenicity of Chloroform in Female B6C3F1 Mice: Comparison of Administration by Gavage in Corn Oil vs ad Libitum in Drinking Water. Larson, J. L., Wolf, D. C., and Butterworth, B. E. (1994). Fundam. Appl. Toxicol. 22, 90-102.Chloroform increases the incidence of liver tumors in B6C3F1 mice when administered in by gavage in corn oil, but not when given in the drinking water at similar daily doses. Since cytotoxicity and regenerative cell proliferation have been implicated in the tumorigenic process for this nongenotoxic agent, these effects of chloroform in corn oil and drinking water were evaluated under conditions similar to the two bioassays. Female B6C3F1 mice were administered oral doses of 0, 3, 10, 34, 90, 238, or 477 mg/kg chloroform dissolved in corn oil 5 days/week for periods of 4 days or 3 weeks, or were continually exposed to chloroform in the drinking water at concentrations of 0, 60, 200, 400, 900, or 1800 ppm for 4 days or 3 weeks, at which time they were necropsied. 5-Bromo-2′-deoxyuridine (BrdU) was delivered via osmotic pumps implanted 3.5 days prior to necropsy. Cell proliferation was evaluated as the percentage of hepatocytes that entered S-phase over 3.5 days (labeling index, LI), measured by immunohistochemical detection of BrdU incorporated into the DNA. Dose-dependent changes included centrilobular necrosis and markedly elevated LI in mice given 238 or 477 mg/kg chloroform in corn oil (the average daily doses that produced tumors in the cancer bioassay). The no-observed-effect level for histopathological changes was 10 mg/kg/day and for induced cell proliferation was 34 mg/kg/day for chloroform given in corn oil. Chloroform given in the drinking water did not increase the hepatic LI after either 4 days or 3 weeks in any of the dose groups, nor were any microscopic alterations observed in the livers, even though the cumulative daily amount of chloroform ingested in the 1800-ppm exposure group was 329 mg/kg/day. The sustained increase in LI in the livers of mice administered hepatocarcinogenic doses of chloroform in corn oil, but not for chloroform in drinking water, is evidence that chloroform-induced mouse liver cancer is secondary to events associated with induced cytolethality and cell proliferation. The triggering of these effects appears to be dependent on both the rate and duration of chloroform delivery to the target tissues. Thus, the most straightforward risk assessment for chloroform for this tissue would assign no increased cancer risk for dosing regimens that do not induce cytolethality and cell proliferation.

Inhibition of rat mononuclear cell leukemia by corn oil gavage: in vivo, in situ and immune competence studies.

Corn oil administered by oral gavage decreases the spontaneous incidence of mononuclear cell leukemia (MNCL) in male Fischer rats used as vehicle controls in long-term carcinogenesis experiments. We used an MNCL transplant model, an in situ MNCL cell proliferation assay and immune competence assays to explore mechanism(s) underlying the effects of corn oil gavage on MNCL development in male rats. Relative to non-gavaged or water-gavaged rats, corn oil-gavaged rats had approximately 25% lower MNCL incidence as well as longer MNCL latency and increased survival. There were no differences in body weight or caloric intake between treatment groups, as corn oil-gavaged rats compensated for calories supplied by the gavaged oil by consuming less food. These data indicate that transplanted MNCL cells grew slower in corn oil-gavaged rats than in non-gavaged or water-gavaged rats and suggest that corn oil gavage may exert its effects through a decrease in protein or other nutrients. Five-day proliferation rates of cultured MNCL cells in diffusion chambers implanted in male corn oil-gavaged rats were 40% less than in water-gavaged rats, suggesting nutrition-sensitive endogenous factors mediate the suppression of MNCL cell proliferation in corn oil-gavaged rats. Corn oil-gavaged rats had 54% lower serum growth hormone (GH) levels, and replacement of GH into corn oil-gavaged rats by osmotic minipump infusion increased in situ MNCL cell proliferation to rates observed in water-gavaged animals. Corn oil-gavaged rats also showed enhanced cellular immune competence as measured by mitogen stimulation, natural cytotoxicity and immunofluorescence assays. Taken together, these findings suggest corn oil administered by oral gavage may decrease MNCL development by slowing MNCL cell proliferation, mediated at least in part by altered levels of diffusible factors such as GH, and/or by enhancing immune competence.

Induced Cytotoxicity and Cell Proliferation in the Hepatocarcinogenicity of Chloroform in Female B6C3F1 Mice: Comparison of Administration by Gavage in Corn Oil vs ad Libitum in Drinking Water

Chloroform increases the incidence of liver tumors in B6C3F mice when administered in by gavage in corn oil, but not when given in the drinking water at similar daily doses. Since cytotoxicity and regenerative cell proliferation have been implicated in the tumorigenic process for this nongenotoxic agent, these effects of chloroform in corn oil and drinking water were evaluated under conditions similar to the two bioassays. Female B6C3F mice were administered oral doses of 0, 3, 10, 34, 90, 238, or 477 mg/kg chloroform dissolved in corn oil 5 days/week for periods of 4 days or 3 weeks, or were continually exposed to chloroform in the drinking water at concentrations of 0, 60, 200,400, 900, or 1800 ppm for 4 days or 3 weeks, at which time they were necropsied. 5-Bromo-2'-deoxyuridine (BrdU) was de livered via osmotic pumps implanted 3.5 days prior to necropsy. Cell proliferation was evaluated as the percentage of hepato cytes that entered S-phase over 3.5 days (labeling index, LI), measured by immunohistochemical detection of BrdU incorporated into the DNA. Dose-dependent changes included centrilobular necrosis and markedly elevated LI in mice given 238 or 477 mg/kg chloroform in corn oil (the average daily doses that produced tumors in the cancer bioassay). The no-observed-effect level for histopathological changes was 10 mg/kg/day and for induced cell proliferation was 34 mg/kg/day for chloroform given in corn oil. Chloroform given in the drinking water did not increase the hepatic LI after either 4 days or 3 weeks in any of the dose groups, nor were any microscopic alterations observed in the livers, even though the cumulative daily amount of chloro form ingested in the 1800-ppm exposure group was 329 mg/kg/ day. The sustained increase in LI in the livers of mice administered hepatocarcinogenic doses of chloroform in corn oil, but not for chloroform in drinking water, is evidence that chloroform-induced mouse liver cancer is secondary to events associated with induced cytolethality and cell proliferation. The triggering of these effects appears to be dependent on both the rate and duration of chloroform delivery to the target tissues. Thus, the most straightforward risk assessment for chloroform for this tissue would assign no increased cancer risk for dosing regimens that do not induce cytolethality and cell proliferation.

Dose Response for TCDD Promotion of Hepatocarcinogenesis in Rats Initiated with DEN: Histologic, Biochemical, and Cell Proliferation Endpoints

The present study examines the dose-response relationship for 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) promotion of histologic and biochemical parameters by using a two-stage model for hepatocarcinogenesis in female Sprague-Dawley rats initiated with a single intraperitoneal dose of 175 mg of diethylnitrosamine (DEN)/kg body weight at 70 days of age. Starting 2 weeks after initiation, treatment groups of 8-10 rats were given TCDD by gavage in corn oil once every 2 weeks for 30 weeks. Doses were 3.5, 10.7, 35.7, and 125 ng TCDD/kg body weight/day. A significant body weight reduction was present in the noninitiated group that received 125 ng TCDD. Relative liver weight was statistically increased in initiated rats treated with > or = 10.7 ng TCDD and in noninitiated rats treated with > or = 35.7 ng TCDD. Histopathologic evidence of cytotoxicity was dose-related in all TCDD-treated groups. There was a statistically significant dose response in the bromodeoxyuridine (BrdU) S-phase labeling index (LI) in the DEN-initiated rats (p < 0.01) and a marginally significant trend in the saline-treated rats (p = 0.10), but proliferating cell nuclear antigen S-phase LI and growth fraction within altered hepatic foci showed no increase. Among the DEN-initiated groups there was a significant increase in glutathione S-transferase altered hepatic foci stereological parameters in the 125 ng TCDD group. This study demonstrates that dose-response relationships for TCDD's effects on cell proliferation growth of altered hepatic foci are different from previously reported effects on P450 gene expression, indicating that different biological or biochemical responses may exhibit different dose-response relationships.(ABSTRACT TRUNCATED AT 250 WORDS)

Dose response for TCDD promotion of hepatocarcinogenesis in rats initiated with DEN: histologic, biochemical, and cell proliferation endpoints.

The present study examines the dose-response relationship for 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) promotion of histologic and biochemical parameters by using a two-stage model for hepatocarcinogenesis in female Sprague-Dawley rats initiated with a single intraperitoneal dose of 175 mg of diethylnitrosamine (DEN)/kg body weight at 70 days of age. Starting 2 weeks after initiation, treatment groups of 8-10 rats were given TCDD by gavage in corn oil once every 2 weeks for 30 weeks. Doses were 3.5, 10.7, 35.7, and 125 ng TCDD/kg body weight/day. A significant body weight reduction was present in the noninitiated group that received 125 ng TCDD. Relative liver weight was statistically increased in initiated rats treated with > or = 10.7 ng TCDD and in noninitiated rats treated with > or = 35.7 ng TCDD. Histopathologic evidence of cytotoxicity was dose-related in all TCDD-treated groups. There was a statistically significant dose response in the bromodeoxyuridine (BrdU) S-phase labeling index (LI) in the DEN-initiated rats (p < 0.01) and a marginally significant trend in the saline-treated rats (p = 0.10), but proliferating cell nuclear antigen S-phase LI and growth fraction within altered hepatic foci showed no increase. Among the DEN-initiated groups there was a significant increase in glutathione S-transferase altered hepatic foci stereological parameters in the 125 ng TCDD group. This study demonstrates that dose-response relationships for TCDD's effects on cell proliferation growth of altered hepatic foci are different from previously reported effects on P450 gene expression, indicating that different biological or biochemical responses may exhibit different dose-response relationships.(ABSTRACT TRUNCATED AT 250 WORDS)

Residual Myelotoxicity of Lindane in Mice

Residual Myelotoxicity of Lindane in Mice. Hong, H. L., and Boorman, G. A. (1993). Fundam. Appl. Toxicol. 21, 500-507.Lindane (γ-1,2,3,4,5,6-hexachlorocyclohexane), a widely used insecticide, may be found at low concentrations in the human diet. Male B6C3F1 mice given lindane daily at doses of 20 and 40 mg/kg body wt by gavage in corn oil for 3 days had suppressed bone marrow cellularity, erythrocyte precursors, granulocyte-macrophage progenitor cells (CFU-GM), and residual progenitor cell damage, which could be demonstrated by two whole-body irradiations (WBI) at 200 rads. Lindane exposure for 10 consecutive days at doses of 0, 10, or 20 mg/kg did not cause clinical abnormality or changes in body weights, but there were dose-dependent decreases in marrow cellularity, in more pluripotent stem cells and in committed CFU-GMs, which returned to control values by 4 weeks. These mice were then subjected to two 100-rad exposures of WBI at 4 and 9 weeks following cessation of lindane treatment. This level of irradiation caused only a transient drop in number of marrow progenitor cells. Control and lindane-exposed mice were examined at 1 and 6 weeks following the last irradiation, which was 10 and 15 weeks following the final lindane exposure. The lindane-exposed mice had lower progenitor cell numbers and slower recovery from the irradiation. These results indicate that lindane has significant myelotoxicity in mice and short-term lindane exposure can induce residual progenitor cell damage that can be demonstrated by subsequent irradiation.

Toxicity of 1,1,1‐trichloro‐2‐propanone in Sprague‐Dawley rats

1,1,1-Trichloro-2-propanone (1,1,1-TCP) has been identified as a chlorination by-product in finished drinking water supplies. Since little was known of its oral toxicity, exposure studies were conducted with male and female Sprague-Dawley rats (10 males and 10 females/group) exposed by corn oil gavage at 0, 16, 48, 161, or 483 mg/kg for 10 d or 0, 30, 90, or 270 mg/kg for 90 d. Evaluations included mortality, clinical signs, body weight, food consumption, ophthalmology, hematology, clinical chemistry, urinalysis, organ weights, gross pathology, and histopathology. In the 10-d study, severe toxicity was observed at the highest dose level, since most treated animals (8/10 males and 7/10 females) died. Toxicity was also noted at 161 and 48 mg/kg. At 161 mg/kg, 2 males died and an increase in liver weights in both sexes was observed. Acanthosis and hyperkeratosis of the forestomach was present in males and females at 48 mg/kg and above. In the 90-d study, toxicity was significant at 270 mg/kg, with acanthosis and hyperkeratosis of the forestomach evident in most animals and ataxia in about one-half of them. Retinal degeneration, increased serum potassium, and increased blood urea nitrogen were present in females and increased blood calcium in males at that same dose level. Acanthosis and hyperkeratosis were observed in both sexes, and retinal degeneration was prominent in 2 females at 90 mg/kg. It was concluded that 16 mg/kg was the NOAEL (no observed adverse effect level) for the 10-d study while 30 mg/kg was the NOAEL for the 90-d exposure of Sprague-Dawley rats to 1,1,1,-trichloro-2-propanone.

Comparison of the toxicity of citral in F344 rats and B6C3F 1 mice when administered by microencapsulation in feed or by corn-oil gavage

A study of the potential effects of microencapsulation on the toxicity of citral was conducted in 14-day continuous feeding studies with both sexes of F344 rats and B6C3F 1 mice. Toxicity by the feeding route was compared with that from bolus doses of the neat chemical in corn oil administered by gavage. Both sexes of rats and mice were given diet containing 0, 0.63, 1.25, 2.5, 5 and 10% citral microcapsules. These feed formulations were equivalent to daily doses of 0, 142, 285, 570, 1140 and 2280 mg citral/kg body weight for rats and 0, 534, 1068, 2137, 4275 and 8550 mg citral/kg body weight for mice. The daily gavage doses were 0, 570, 1140 and 2280 mg citral/kg body weight for both sexes of rats, and 0, 534, 1068 and 2137 mg citral/kg body weight for both sexes of mice. Citral microcapsules administered in the diet did not cause mortality in mice or rats. Toxicity was confined to decreases in body weight at the 10% concentration in mice, at the 5 and 10% concentrations in rats, and decreases in absolute weights of the liver, kidney and spleen at the 10% concentration in rats. The only histopathological change observed was minimal to mild hyperplasia and/or squamous metaplasia of the respiratory epithelium in the anterior portion of the nasal passages of rats fed 5 or 10% citral microcapsules. By contrast, citral gavage caused mortality in five out of five male and female mice at 2137 mg/kg body weight, and in two out of five male mice at 1068 mg/kg body weight. There were dose-related increases in absolute liver weights of male and female mice. Cytoplasmic vacuolization of hepatocytes occurred in all female mice gavaged with 1068 and 2137 mg citral/kg body weight, and in male mice from the 2137 mg/kg dose group. Necrosis, ulceration and/or acute inflammation of the forestomach occurred in the high-dose mice of both sexes. Inflammation and/or hyperplasia of the forestomach occurred in about half of the male and female mice dosed with 1068 mg citral/kg. Citral gavage at doses that were equivalent to up to 10% in the diet (2280 mg/kg body weight) did not cause toxicity in rats, except for minimal hyperplasia of the squamous epithelium of the forestomach in high-dose males. Microencapsulated citral given in the diet has distinct advantages as an alternative route of administration for long-term studies: the microencapsulation process prevents the normally rapid degradation of the chemical; continual ingestion from the diet mimics the human route of exposure; and higher doses of the chemical can be attained in the animal model to maximize the detection of potential toxic or carcinogenic responses.

Assessment of the Carcinogenic Potential of Chlorinated Water: Experimental Studies of Chlorine, Chloramine, and Trihalomethanes

Water chlorination has been one of the major disease prevention treatments of this century. While epidemiologic studies suggest an association between cancer in humans and consumption of chlorination byproducts in drinking water, these studies have not been adequate to draw definite conclusions about the carcinogenic potential of the individual byproducts. The purpose of this study was to investigate the carcinogenic potential of chlorinated or chloraminated drinking water and of four organic trihalomethane byproducts of chlorination (chloroform, bromodichloromethane, chlorodibromomethane, and bromoform) in rats and mice. Bromodichloromethane, chlorodibromomethane, bromoform, chlorine, or chloramine was administered to both sexes of F344/N rats and (C57BL/6 x C3H)F1 mice (hereafter called B6C3F1 mice). Chloroform was given to both sexes of Osborne-Mendel rats and B6C3F1 mice. Chlorine or chloramine was administered daily in the drinking water for 2 years at doses ranging from 0.05 to 0.3 mmol/kg per day. The trihalomethanes were administered by gavage in corn oil at doses ranging from 0.15 to 4.0 mmol/kg per day for 2 years, with the exception of chloroform, which was given for 78 weeks. The trihalomethanes were carcinogenic in the liver, kidney, and/or intestine of rodents. There was equivocal evidence for carcinogenicity in female rats that received chlorinated or chloraminated drinking water; this evidence was based on a marginal increase in the incidence of mononuclear cell leukemia. Rodents were generally exposed to lower doses of chlorine and chloramine than to the trihalomethanes, but the doses in these studies were the maximum that the animals would consume in the drinking water. The highest doses used in the chlorine and chloramine studies were equivalent to a daily gavage dose of bromodichloromethane that induced neoplasms of the large intestine in rats. In contrast to the results with the trihalomethanes, administration of chlorine or chloramine did not cause a clear carcinogenic response in rats or mice after long-term exposure. These results suggest that organic byproducts of chlorination are the chemicals of greatest concern in assessment of the carcinogenic potential of chlorinated drinking water.

Acute hepatotoxic and nephrotoxic effects of chloroform in male F-344 rats and female B6C3F1 mice

Previous studies demonstrated that chloroform given by oral gavage in corn oil caused an increased incidence of liver tumors in male and female mice and kidney tumors in male rats, while administration in drinking water resulted in an increased tumor incidence only in the kidneys of the male rats. The tumorigenicity of this nongenotoxic agent has been postulated to be linked with cytolethality and cell proliferation. This study examined the organ-specific toxicity of acute doses of chloroform. Male F-344 rats were given chloroform by gavage in corn oil at the bioassay doses of chloroform of 0 and 180 mg/kg body wt as well as 34 and 477 mg/kg and necropsied 24 hr later. Additional rats were given a single dose of 180 mg chloroform/kg and administered bromodeoxyuridine (BRDU) 2 hr prior to necropsy at 0.5, 1, 2, 4, and 8 days after chloroform treatment. Female B6C3F1 mice were given chloroform by gavage at the bioassay doses of 0, 238, and 477 mg/kg as well as 34 mg/kg and necropsied at 24 hr after treatment. Additional mice were given a single dose of 350 mg chloroform/kg, labeled with BRDU, and necropsied at 0.5, 1, 2, 4, and 8 days after treatment. The kidneys of male rats administered 34, 180, and 477 mg chloroform/kg exhibited mild to severe proximal tubular necrosis in a dose-dependent manner. A 20-fold increase in the labeling index (LI, the percentage of nuclei in S-phase) in the proximal tubule cells was observed 2 days after treatment with the bioassay dose of 180 mg/kg. The livers of male rats exhibited only slight to moderate multifocal centrilobular necrosis at 180 and 477 mg/kg. A 10-fold increase in the LI was observed in the liver of male rats given 477 mg/kg, but no increase was observed at the bioassay dose of 180 mg/kg. In contrast to male rats, female mice developed a dose-dependent centrilobular hepatic necrosis at 238 and 477 mg/kg. No renal lesions were observed in female mice at any dose. A peak increase in LI of 38-fold was observed in hepatocytes in the livers of female mice 2 days after treatment with 350 mg chloroform/kg, with only a 2-fold increase in LI observed in the kidneys. These data indicate that acute chloroform-induced cytolethality leads to increased cell proliferation and that the organ-specific pattern of toxicity is the same as the organ-specific pattern of tumor formation.(ABSTRACT TRUNCATED AT 400 WORDS)

Influence of corn oil and diet on body weight, survival, and tumor incidences in F344/N rats

Amount and type of fat and energy density of diets may influence tumor incidences. The purpose of this report is to summarize the influence of corn oil gavage and different nonpurified diets on spontaneous tumor incidences in 64 diet and 59 corn oil gavage control groups in two-year studies involving approximately 6,100 control Fischer 344 rats of each sex. The maximum mean body weight attained during the course of the study, survival at 106 weeks of age, and spontaneous tumor incidences of groups fed different nonpurified diets with or without corn oil gavage were summarized and evaluated for differences. Male rats fed NIH-07 open-formula diet with or without corn oil gavage had significantly higher body weight, lower survival, and higher incidence of pancreatic acinar cell tumors than rats fed commercial proprietary diets with or without corn oil gavage. Female rats fed NIH-07 diet with or without corn oil gavage had significantly higher body weights and pancreatic tumor incidences than groups fed commercial diets. Time-related trends could account for other apparent differences in tumor incidences between the groups fed commercial and NIH-07 diets. Corn oil gavage significantly increased the body weight and pancreatic tumor incidences but decreased the incidence of leukemia, a lethal tumor, which resulted in higher survival in male rats. Corn oil gavage significantly lowered the body weight and anterior pituitary tumor incidence in female rats. The pancreatic acinar cell tumor incidence appears to be due to a combination of fat intake and body weight.

Acute Hepatotoxic and Nephrotoxic Effects of Chloroform in Male F-344 Rats and Female B6C3F1 Mice

Previous studies demonstrated that chloroform given by oral gavage in corn oil caused an increased incidence of liver tumors in male and female mice and kidney tumors in male rats, while administration in drinking water resulted in an increased tumor incidence only in the kidneys of the male rats. The tumorigenicity of this nongenotoxic agent has been postulated to be linked with cytolethality and cell proliferation. This study examined the organ-specific toxicity of acute doses of chloroform. Male F-344 rats were given chloroform by gavage in corn oil at the bioassay doses of chloroform of 0 and 180 mg/kg body wt as well as 34 and 477 mg/kg and necropsied 24 hr later. Additional rats were given a single dose of 180 mg chloroform/kg and administered bromodeoxyuridine (BRDU) 2 hr prior to necropsy at 0.5, 1, 2, 4, and 8 days after chloroform treatment. Female B6C3F1 mice were given chloroform by gavage at the bioassay doses of 0, 238, and 477 mg/kg as well as 34 mg/kg and necropsied at 24 hr after treatment. Additional mice were given a single dose of 350 mg chloroform/kg, labeled with BRDU, and necropsied at 0.5, 1, 2, 4, and 8 days after treatment. The kidneys of male rats administered 34, 180, and 477 mg chloroform/kg exhibited mild to severe proximal tubular necrosis in a dose-dependent manner. A 20-fold increase in the labeling index (LI, the percentage of nuclei in S-phase) in the proximal tubule cells was observed 2 days after treatment with the bioassay dose of 180 mg/kg. The livers of male rats exhibited only slight to moderate multifocal centrilobular necrosis at 180 and 477 mg/kg. A 10-fold increase in the LI was observed in the liver of male rats given 477 mg/kg, but no increase was observed at the bioassay dose of 180 mg/kg. In contrast to male rats, female mice developed a dose-dependent centrilobular hepatic necrosis at 238 and 477 mg/kg. No renal lesions were observed in female mice at any dose. A peak increase in LI of 38-fold was observed in hepa-tocytes in the livers of female mice 2 days after treatment with 350 mg chloroform/kg, with only a 2-fold increase in LI observed in the kidneys. These data indicate that acute chloroform-induced cytolethality leads to increased cell proliferation and that the organ-specific pattern of toxicity is the same as the organ-specific pattern of tumor formation. These observations are suggestive of a role for induced cell proliferation in tumor formation and indicate that more extensive cell proliferation Studies are Warranted.

The effect of chlorinated paraffins on hepatic enzymes and thyroid hormones

Male rats and mice were administered chlorinated paraffins (CPs) by daily gavage in corn oil for 14 days. Chlorowax 500C (short chain CP with 58% chlorination), Cereclor 56L (short chain CP with 56% chlorination) and Chlorparaffin 40G (medium chain CP with 40% chlorination) were the CPs studied at dose levels of 0, 10, 50, 100, 250, 500 and 1000 mg/kg for both rats and mice. The no effect levels for hepatic perixisome proliferation for the above chemicals, as determined by the CN − insentive palmitoyl co-enzyme A β-oxidation (PCO) assay, were calculated as 184, 600 and 473 mg/kg and 180, 120 and 252 mg/kg for rats and mice, respectively, whilst those for percent liver weight/body weight were calculated as 74, 51 and 31 mg/kg and 215, 70 and 426 mg/kg for rats and mice, respectively. The short chain CPs were more potent peroxisome proliferations than the medium chain CP, with the mouse proving to be more responsive thn the rat. Rats administered the highest dose of CPs showed a depressed plasma thyroxine (T 4) level, with a concomitant increase in the plasma concentrations of thyroid stimulating hormone (TSH). The decrease plasma T 4 levels appeared to be the result of increased T 4 glucuronidition.

Comparative metabolism of phenanthrene in the rat and guinea pig.

In the present study the biotransformation of phenanthrene in the rat and guinea pig was investigated. 14C-labelled phenanthrene was administered by gavage in corn oil to Sprague-Dawley rats (10 mg/kg b.w./day) and guinea pigs (10 mg/kg b.w./day). Urine and feces were separately collected for the determination of the radioactivity content, and pooled urine was used for the analysis of metabolites. Phenanthrene was metabolized by the rat and guinea pig to free hydroxylated phenanthrenes and their conjugates. The percentages of conjugates, expressed as the total urinary radioactivity, were 39% glucuronides, 24% sulfates and 18% cysteinylglycine for rats; and 39% glucuronides, 23% sulfates and 28% cysteinylglycine for guinea pigs. Enzymatic hydrolysis of glucuronides and sulfates resulted in the formation of free 1,2-, 3,4- and 9,10-dihydrodiols of phenanthrene and 1-, 2-, 3-, and 4-hydroxyphenanthrene in both species.

Value of Historical Controls in the Interpretation of Rodent Tumor Data

In long term rodent carcinogenicity studies, the concurrent control group is the primary control group for data evaluation. However, there are instances in which the use of historical control data can help in the interpretation of experimental results, such as rare tumors and marginally increased tumor rates relative to concurrent controls. However, if historical control data are to be utilized in a formal testing framework, it is important that studies in the database be similar to the concurrent controls with respect to the factors known to influence tumor occurrence. These include dietary factors/body weight gain, gross necropsy and slide preparation procedures, histopathologic diagnosis, and study duration/survival of animals. Different types of control groups (eg, untreated and corn oil gavage) may also have different tumor rates. Time-related trends and inter-laboratory variability in tumor rates frequently observed in long term rodent studies are likely attributable to these factors. Examples are g...

Application of molecular encapsulation for toxicology studies: Comparative toxicity of p-chloro-α,αmα-trifluorotoluene in α-cyclodextrin vehicle versus corn oil vehicle in male and female Fischer 344 rats and B6C3F1 mice

The application of α-cyclodextrin (α-CD) as an alternative vehicle for water insoluble and volatile chemicals was investigated in toxicity studies of p-chloro-α,α,α-trifluorotoluene (CTFT). Groups of F344 rats and B6C3F1 mice of each sex were administered CTFT (97% pure) by gavage in either corn oil or α-CD aqueous formulations daily for 14 consecutive days. The dose levels used were 10 (mice only), 50, 400, and 1000 mg/kg for corn oil vehicle and 10, 50, and 400 mg/kg (maximum achievable dose at gavage volume of 5 ml/kg) for α-CD vehicle. With both vehicles CTFT and α 2u-globulin were found to accumulate in the male rat kidney after 14 days of exposure and a dose-related toxic nephropathy was observed at dose of 50 mg/kg or higher. The hepatocellular hypertrophy and cytoplasmic vacuolation of the adrenal cortex which appeared in dosed male and female rats were also found to be independent of vehicle. Clinical pathology findings suggested a mild anemia and cholestasis in rats. With both vehicles no tissue bioaccumulation of CTFT was found in male or female mice. Vehicle-independent hepatocellular hypertrophy and cholestasis were also observed in mice at doses of 400 and 1000 mg/kg. In conclusion, the α-CD vehicle does not affect the toxic responses of CTFT in both sexes of both species. The results of the studies suggest that α-CD may be an appropriate alternative vehicle for toxicity studies.